Download Desert Pupfish (Cyprinodon macularius)

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Desert Pupfish (Cyprinodon macularius)
Desert Pupfish
(Cyprinodon macularius)
Legal Status
State: Endangered
Federal: Endangered
Critical Habitat: 51 FR 10842–
Photo courtesy of Margaret Widdowson
10851
Recovery Planning: Desert Pupfish Recovery Plan (USFWS 1993)
Taxonomy
The desert pupfish complex was historically comprised of two
subspecies, the nominal desert pupfish (Cyprinodon macularius
macularius) and the Quitobaquito pupfish (Cyprinodon macularius
eremus), and an undescribed species, the Monkey Spring pupfish
(Cyprinodon sp.) (USFWS 1993). The subspecies are now recognized
as three separate species (USWFS 2010): the desert pupfish (C.
macularius), the Sonoyta (Quitobaquito) pupfish (C. eremus) (Echelle
et al. 2000), and the undescribed Monkey Springs pupfish, which has
since been described and renamed the Santa Cruz pupfish (C.
arcuatus). Recent work (Echelle et al. 2007; Koike et al. 2008) and a
summary by the U.S. Fish and Wildlife Service (USFWS 2010) provide
the evidence that C. macularius and C. eremus are separate species.
The Sonoyta pupfish persists in only two populations: one near the
U.S.–Mexico border at Quitobaquito Springs in Organ Pipe Cactus
National Monument in Arizona, and the other at Rio Sonoyta in
Sonora, Mexico (USFWS 2010). The Santa Cruz pupfish occurs in the
Santa Cruz River basins in southern New Mexico. All other
populations are referred to C. macularius. Descriptions of the species’
physical characteristics can be found in USFWS (1993, 2010).
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Desert Pupfish (Cyprinodon macularius)
Distribution
General
The desert pupfish occurs in desert springs, marshes, and tributary
streams of the lower Gila and Colorado River drainages in Arizona,
California, and Mexico. It also formerly occurred in the slow-moving
reaches of some large rivers, including the Colorado, Gila, San Pedro,
and Santa Cruz.
Distribution and Occurrences within the Plan Area
Historical
Historically, desert pupfish occurred in the lower Colorado River in
Arizona and California, from about Needles downstream to the Gulf of
Mexico and onto its delta in Sonora and Baja (CVAG 2007). In
California, pupfish inhabited springs, seeps, and slow-moving streams
in the Salton Sink basin, and backwaters and sloughs along the
Colorado River. Desert pupfish also occurred in the Gila River Basin in
Arizona and Sonora, including the Gila, Santa Cruz, San Pedro, and Salt
Rivers; the Rio Sonoyta of Arizona and Sonora; Puerto Penasco,
Sonora; and the Laguna Salada Basin of Baja California.
Recent
Because C. eremus and C. arcuatus are now considered separate
species and occur only in southern Arizona and Mexico (USFWS
2010), their distribution information is not discussed further; C.
macularius is described within the Plan Area (see Figure SP-F1).
USFWS (2010) describes that currently five natural populations
persist in California, restricted to two streams tributary to, and a few
shoreline pools and irrigation drains of, the Salton Sea: San Felipe
Creek/San Sebastian Marsh, Salt Creek (within the Dos Palmas
Conservation Area of the Coachella Valley Multiple Species Habitat
Conservation Plan [MSHCP; CVAG 2007]), Salton Sea, irrigation drains
of the Salton Sea, and a wash near Hot Mineral Spa (a natural
population added since the 1993 recovery plan). The desert pupfish
population in Salt Creek is stable to increasing, and currently has few
non-native species (Keeney 2010a, cited in USFWS 2010). San Felipe
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Desert Pupfish (Cyprinodon macularius)
Creek also has a stable to increasing population, and no nonnative fish
have been found in recent surveys (USFWS 2010). In addition, there
are a number of refugium or captive populations of desert pupfish in
California at a variety of sites (USFWS 2010): Anza-Borrego State
Park; Oasis Springs Ecological Reserve; Salton Sea State Recreation
Area; Dos Palmas Reserve; Living Desert Museum; University of
California, Riverside; and Borrego Springs High School. The Coachella
Valley MSHCP (CVAG 2007) also describes a refugium population in
the larger pools around the Thousand Palms oasis area.
Natural History
Habitat Requirements
Found in shallow water of desert springs, small streams, and
marshes below 1,515 meters (5,000 feet) elevation (USFWS 1993),
this species tolerates high salinities, high water temperatures, and
low dissolved-oxygen concentrations. According to the Imperial
Irrigation District and Bureau of Reclamation (2002, cited in Black
1980; USFWS 1993), pupfish typically prefer clear water, with either
rooted or unattached aquatic plants, restricted surface flow, or
sand–silt substrates. Pupfish use shallow water habitats extensively,
often occupying such habitat at temperatures that are above the
thermal optimum for invasive fishes. Pupfish do well if these
habitats have little vegetation apart from mats of benthic algae over
a fine-grained mineral or detrital substrate; they also utilize areas
with aquatic or emergent vascular vegetation (ICF 2009). Desert
pupfish in general are noted for their tolerance of environmental
stress; they can tolerate dissolved-oxygen concentrations as low as
0.13 parts per million (Helfman et al. 1997). Their temperature
tolerance ranges from a low of 4.4°C (Schoenherr 1990) to a high of
42.4°C (Carveth et al. 2006). Their salinity tolerance ranges from 0 to
70 parts per trillion for eggs and adults (Barlow 1958; Schoenherr
1988) and up to 90 parts per trillion for larvae (Schoenherr 1988).
Martin and Saiki (2005) found that desert pupfish abundance was
higher when vegetative cover, pH, and salinity were high and when
sediment factor and dissolved oxygen were low. They hypothesize
that water quality extremes (especially high pH and salinity, and low
dissolved oxygen) limit the occurrence of nonnative fishes.
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Desert Pupfish (Cyprinodon macularius)
Table 1. Habitat Associations for Desert Pupfish
Land Cover
Type
Shallow water
of desert
springs, small
streams, and
marshes
Land
Cover Use
Breeding/
foraging
Habitat
Designation
Primary
habitat
Habitat
Parameters
Clear water, with
either rooted or
unattached
aquatic plants,
restricted surface
flow, or sand–silt
substrates
Supporting
Information
Direct
observational
studies
________________
Sources: Black 1980; USFWS 1993; Martin and Saiki 2005.
Foraging Requirements
Pupfish are opportunistic omnivores, thriving on a diet of algae,
aquatic plants, detritus, and small invertebrates (Sutton 1999, citing
Crear and Haydock 1971 and Naiman 1979). Adult foods include
ostracods, copepods, and other crustaceans and insects; pile worms;
mollusks; and bits of aquatic macrophytes torn from available tissues
(USFWS 1993). Detritus or algae are often predominant in their
diets (USFWS 1993). Pit digging, the active excavation of soft bottoms
in search of food, is a pupfish behavior described by Minckley and
Arnold (1969); these pits are defended when occupied. Foraging is
typically a daytime activity, and fish may move in response to daily
warming from shallower water during morning to feed in deeper
places later in the day (USFWS 1993).
Reproduction
Desert pupfish may become sexually mature as early as 6 weeks of age
at 1.5 centimeters in length under conditions of abundant food and
suitable temperature. Although they may breed during their first
summer, most do not breed until their second summer, when their
length may have reached a maximum of 7.5 centimeters (Moyle 2002).
In favorable conditions a pair of pupfish can produce 800 eggs in a
season (ICF 2009). Eggs appear to be randomly deposited within the
male territory. Although males actively patrol and defend individual
territories, there is no directed parental care (USFWS 1993).
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Desert Pupfish (Cyprinodon macularius)
Dec
X
Nov
X
Oct
Aug
X
Sep
July
May
June
Breeding
________________
Source: USFWS 1993.
April
March
Feb
Jan
Table 2. Key Seasonal Periods for Desert Pupfish
Spatial Behavior
The dispersal, home range, and migratory patterns of desert pupfish
are not well understood. Many of the locations where they are
currently found are completely isolated from other populations.
Desert pupfish congregate in the summer where adult females swim
in loose schools and leave the school when attracted by a territorial
male to spawn. Pupfish movement between the Salton Sea and nearby
drains has been observed (Sutton 1999). Sutton (2002) describes
desert pupfish summer movement between a drain (although not
connected directly to the Salton Sea) and a shoreline pool, as well as
movement of approximately 0.5 kilometer (0.3 mile) from Salt Creek
to a downstream shoreline pool (although not connected to the Salton
Sea). Sutton (2002) hypothesizes that movements from Salt Creek to
the shoreline pool were due to water level drops. The technique used
by Sutton (2002) for tracking desert pupfish holds promise for further
desert pupfish movement studies.
Table 3. Spatial Behavior by Desert Pupfish
Type
Breeding
territory
Distance/Area
Normally
defends 1 to 2
square meters
but as large as
5 to 6 square
meters
5
Location of
Study
Not disclosed
Citation
Moyle 1976
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Desert Pupfish (Cyprinodon macularius)
Ecological Relationships
The desert pupfish were once found in varying water bodies from
cienegas and springs to shallow streams and margins of larger bodies
of water where they preferred shallow, slower-moving water with
soft substrates and clear water (USFWS 1993). Over the last century,
land use activities such as groundwater pumping, dewatering, water
diversion, and drain maintenance have altered the water levels,
resulting in habitat loss for desert pupfish. Channel erosion can
increase the sediment in the water, reducing its suitability for the
pupfish; water impoundment creates deeper ponds that increase
occupation by non-native aquatic species; and grazing practices
reduce vegetative cover, increase sedimentation, and trample habitat
(USFWS 1993).
Currently, the major threat to the species is the presence of exotic
aquatic species, particularly tilapia (Tilapia spp.), sailfin molly
(Poecilia latipinna), longjaw mudsucker (Gillichthys mirabilis),
western mosquitofish (Gambusia affinis), several snail species, and
crayfish (Procambarus clarkia). These and other introduced fish
species affect pupfish populations through predation, competition,
and behavioral interference (CVAG 2007).
The desert pupfish appears to go through cycles of expansion and
contraction in response to natural weather patterns (51 FR 10842–
10851; USFWS 1993; Weedman and Young 1997, cited in USFWS
2010). In very wet years, populations can rapidly expand into new
habitats (Hendrickson and Varela-Romero 1989, cited in USFWS
2010). In historical times, this scenario would have led to panmixia
among populations over a very large geographic area (USFWS 1993).
Population Status and Trends
Global: Critically imperiled (NatureServe 2011)
State: Same as above
Within Plan Area: Same as above
In its 5-year review, USFWS (2010) concluded that threats to the
species and their overall level of intensity remain similar to when the
species was originally given a recovery priority number of 2C. Priority
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Desert Pupfish (Cyprinodon macularius)
number 2C is indicative of a high degree of threat, a high potential for
recovery, and taxonomic classification as a species.
Threats and Environmental Stressors
USFWS (2010) summarizes the threats to desert pupfish survival.
These include threats relating to destruction or curtailment of habitat
or range (USFWS Factor A), including loss and degradation of suitable
habitat through groundwater pumping or water diversion;
contamination from agricultural return flows, as well as other
contaminants; and physical changes to water properties involving
suitable water quality. There is no new information to suggest that
overutilization for commercial, recreational, scientific, or educational
purposes (USFWS Factor B) are threats. The effect of disease or
predation (USFWS Factor C) is a potential threat to desert pupfish.
Currently, the specific effects to individual desert pupfish or
populations from disease or parasites are unknown. Predators and
competitors of the desert pupfish include tilapia, sailfin mollies,
shortfin mollies (Poecilia mexicana), mosquitofish, pothole livebearers
(Poeciliposis gruci), and several members of the families
Centrarchidae, Ictaluridae, and Cyprinidae, as well as melianias
(Melanoides tuberculata and Melanoides granifera), crayfish, Rio
Grande leopard frog (Lithobates berlandieri), and bullfrog (Rana
catesbeiana) (51 FR 10842–10851; Black 1980; ICF 2009). Invasive
snails (melianias) consume the algal mats that form the pupfish's
principal food source (ICF 2009); juvenile tilapias compete with
desert pupfish for many of the same food items (Matsui 1981); and
crayfish, frogs and adult tilapia prey on fish and fish eggs (51 FR
10842–10851; ICF 2009; Matsui 1981). Crayfish were thought to be
responsible for elimination of the Owens pupfish, C. radiosus, from a
refugium in Warm Springs near Big Pine, California (Black 1980).
These and other introduced aquatic species affect pupfish populations
through predation, competition, and behavioral interference.
Inadequacy of existing regulatory mechanisms (USFWS Factor D) is a
potential threat to desert pupfish. Regulatory mechanisms exist in
much the same state as at the time of listing, though the application of
recent case law may result in reduced consideration of impacts to
isolated waters containing desert pupfish (USFWS 2010). Finally,
other natural or manmade factors affecting the continued existence of
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desert pupfish (USFWS Factor E) have been noted as a threat for
desert pupfish, including the v and control actions that would likely be
detrimental to pupfish habitat (USFWS 1993). The only new threat
identified is endocrine disruptors noted in the Salton Sea irrigation
drains (USFWS 2010).
Conservation and Management Activities
The Coachella Valley MSHCP (CVAG 2007) lists some conservation
and management actions that would benefit pupfish:
1. Complete hydrologic studies for the Salt Creek area to determine if
the water sources for Salt Creek are adequately protected or if
additional water sources may be needed and are available.
2. Ensure persistence of pupfish populations in agricultural drains by
managing agricultural drain maintenance and water supply.
Monitoring will include surveys for pupfish presence in the
agricultural drains along with regular sampling of flow, water
depth, and selenium concentrations
3. Control and manage exotic or invasive species in pupfish habitat, if
monitoring identifies this as a threat. Control efforts should
address nonnative fish, bullfrogs, and other invasive species. The
presence and potential impacts of Asian tapeworm, a potential
pupfish parasite, shall also be addressed.
a. Remove tamarisk (salt cedar) where it is affecting the
amount of water available to pupfish.
4. Maintain water levels, water quality, and proper functioning
condition of ponds, springs, and drains, to the extent these
activities are under Plan authority, which will include reevaluating
the feasibility of available technologies to reduce selenium
concentrations.
5. Restore and enhance degraded habitat as necessary according to
monitoring results.
6. Conduct experiments on the timing and mechanics of drain
cleaning that would minimize impacts to desert pupfish.
7. Estimate distribution and/or population size of desert pupfish.
8. Survey contaminant levels in the water and in pupfish.
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USFWS (2010) also lists some general future conservation and
management activities:
•
A specific standardized genetic protocol should be developed,
using work by Echelle et al. (2007), as a template for
management of C. macularius refuge populations. Their
recommendations include establishing large primary refuge
populations, with each one representing the groups of wild C.
macularius. They also recommend that secondary refuges
representing each of the wild source regions be established.
•
A recovery plan amendment or revision should be made based
on recommendations by Loftis et al. (2009) that delineate a
different set of management units in the Salton Sea than is
recognized in the existing recovery plan and to reflect the
changed taxonomy.
•
Conservation at wild sites should be emphasized.
•
A Safe Harbor Agreement or similar tool for the desert pupfish
in California should be pursued.
Data Characterization
Loftis et al. (2009) assessed the mitochondrial DNA (mtDNA) results
from the 1997 and 1998 surveys by Echelle et al. (2000) and used
data from 10 microsatellite DNA loci to describe the genetic structure
of the two extant species (C. macularius and C. eremus). According to
Loftis et al., this data showed that there “was evidence (RST>FST) that
the two extant populations of C. eremus have been isolated sufficiently
long for mutation to contribute significantly to genetic divergence,
whereas divergence among the nine assayed populations of C.
macularius could be attributed to genetic drift alone.” The assessment
suggests that based on variability among the mtDNA, there are two
populations of C. eremus and five groups of populations of C.
macularius that should be managed as units for conservation genetics
management of the two species.
The distribution of the species and principal threats to its continued
existence are sufficiently well known to allow coverage of this species
in the Desert Renewable Energy Conservation Plan.
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Management and Monitoring Considerations
As summarized above, the Coachella Valley MSHCP (CVAG 2007) lists
some specific conservation and management actions for the Plan Area
that would benefit pupfish. In addition, invasive species management
options for the Dos Palmas Area of Critical Environmental Concern
have been prepared (ICF 2009) and cover threats to the desert
pupfish. Within that document, specific management actions that may
be used to eliminate non-native aquatic species or create predatorfree environments are evaluated; these include water management
that alternately inundates and desiccates habitat, creation of channel
habitat, creation of shallow-water habitat, removal and/or burning of
emergent aquatic habitat, and invasive aquatic species trapping. The
Desert Pupfish Recovery Plan (USFWS 1993) emphasizes securing
extant wild populations of desert pupfish to preserve original genetic
material, and creating a second and third tier of populations from
these existing wild populations using a genetic exchange protocol that
would be created to mimic desert pupfish evolution. Refuge
population or new habitat may not be difficult to create as is
evidenced by the shallow-water habitat that was constructed near the
Alamo River, which was designed to exclude fish; however, desert
pupfish got into the ponds and flourished (Roberts 2010, cited in
USFWS 2010; Saiki et al. 2011).
Predicted Species Distribution in Plan Area
There are 52,438 acres of modeled suitable habitat for desert
pupfish in the Plan Area. Modeled suitable habitat occurs in the
Imperial Valley. Modeled suitable habitat includes seeps/springs,
perennial
streams/rivers,
perennial
lakes/ponds,
and
swamps/marshes, as well as the area along the edge of the Salton
Sea. Specific model parameters and a figure showing the modeled
suitable habitat in the Plan Area are included in Appendix C.
Literature Cited
51 FR 10842–10851. Final Rule: “Endangered and Threatened
Wildlife and Plants Determination of Endangered Status and
Critical Habitat for the Desert Pupfish.” March 31, 1986.
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Barlow, G.W. 1958. “High Salinity Mortality of Desert Pupfish
Cyprinodon Macularius.” Copeia 1958:231–232.
Black, G.F. 1980. Status of the Desert Pupfish, Cyprinodon
Macularius (Baird and Girard), in California. Sacramento,
California: State of California, Department of Fish and Game,
Inland Fisheries Endangered Species Program. Special
Publication 80-1. March 1980.
Carveth, C.J., A.M. Widmar, and S.A. Bonar. 2006. “Comparisons of
Upper Thermal Tolerances of Native and Nonnative Fish in
Arizona.” Transactions of the American Fisheries Society
135(6):1433–1440.
CVAG (Coachella Valley Association of Governments). 2007. The
Coachella Valley Multiple Species Habitat Conservation Plan.
Helfman, G.S., B.B. Collette, and D.E. Facey. 1997. The Diversity of
Fishes. Malden, Massachusetts: Blackwell Science.
ICF. 2009. Invasive Species Management Options for the Dos Palmas
Area of Critical Environmental Concern. Prepared for the
Coachella Valley Conservation Commission.
Imperial Irrigation District and the U.S. Bureau of Reclamation. 2002.
Imperial Irrigation District Water Conservation and Transfer
Project and Habitat Conservation Plan Draft Environmental
Impact Report/Environmental Impact Statement.
Koike, H., A.A. Echelle, D. Loftis, and R.A. Van Den Bussche. 2008.
“Microsatellite DNA Analysis of Success in Conserving Genetic
Diversity after 33 Years of Refuge Management for the Desert
Pupfish Complex.” Animal Conservation 11(2008):321–329.
Loftis, D.G., A.A. Echelle, H. Koike, R.A. Van den Bussche, and C.O.
Minckley. 2009. “Genetic Structure of Wild Populations of the
Endangered Desert Pupfish Complex (Cyprinodontidae:
Cyprinodon).” Conservation Genetics 10:453–463.
Martin, B.A., and M.K. Saiki. 2005. “Relation of Desert Pupfish
Abundance to Selected Environmental Variables in Natural and
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Desert Pupfish (Cyprinodon macularius)
Manmade Habitats in the Salton Sea Basin.” Environmental
Biology of Fishes 73:97–107.
Matsui, M. 1981. The Effects of Introduced Teleost Species on the Social
Behavior of Cyprinodon Macularius Californiensis. Master’s
Thesis. Los Angeles, California: Occidental College.
Minckley, W.L., and E.T. Arnold. 1969. “‘Pit Digging,’ a Behavioral
Feeding Adaptation in Pupfishes (Genus Cvprinodon).” Journal
of the Arizona Academy of Science 4:254–257.
Moyle, P.B. 1976. Inland Fishes of California. Berkeley and Los Angeles:
University of California .
Moyle, P.B. 2002. Inland Fishes of California (Revised and Expanded).
London, United Kingdom: University of California Press Ltd.
NatureServe. 2011. “Cyprinodon Macularius.” NatureServe Explorer: An
Online Encyclopedia of Life. Version 7.1. Arlington, Virginia:
NatureServe. Last updated July 2011. Accessed December
2011. http://www.natureserve.org/explorer.
Saiki, M.K., B.A. Martin, and T.W. Anderson. 2011. “Unusual
Dominance by Desert Pupfish (Cyprinodon Macularius) in
Experimental Ponds within the Salton Sea Basin.” The
Southwestern Naturalist 56(3):385–392.
Schoenherr, A.A. 1988. “A Review of the Life History and Status of the
Desert Pupfish (Cyprinodon Macularius).” Bull. S. Acad. Sci.
81:104–134.
Schoenherr, A.A. 1990. A Comparison of Two Populations of the
Endangered Pupfish (Cyprinodon Macularius). Second annual
report. California Department of Fish and Game.
Sutton, R. 1999. The Desert Pupfish of the Salton Sea: A Synthesis.
Prepared for the Salton Sea Authority. August 5, 1999.
Sutton, R. 2002. “Summer Movements of Desert Pupfish among
Habitats at the Salton Sea.” Hydrobiologia 473:223–228.
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USFWS. 1993. Desert Pupfish (Cyprinodon Macularius) Recovery Plan.
Unpublished report to U.S. Fish and Wildlife Service, Region 2,
Albuquerque, New Mexico, with assistance from Arizona
Game and Fish Department and Tonto National Forest.
September 1993.
USFWS. 2010. Desert Pupfish (Cyprinodon Macularius) 5-Year Review:
Summary and Evaluation. Phoenix, Arizona: USFWS.
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Species Range
in California
Utah
Nevada
!
(
!
(
Current Occurrence Point
Historic and Unknown
Occurrence Point
Note: Occurrence point size
graphically represents the
precision level code for the
data point but is not scaled
geographically.
!
(
Arizona
!
(
!
(
P a c i f i c
Z:\Projects\CEC\j6668_DRECP\MAPDOC\MAPS\BaselineBioReport\SpeciesProfiles
O c e a n
I
!
(
(
!
(!
!
(
!
(
ME X IC O
0
12.5
25
Miles
Sources: DRECP Species Occurrence Database (2011),
CWHR (2008), CEC (2010), USGS (2010), ESRI (2010)
FIGURE SP-F1
Desert Pupfish Occurrences in the Plan Area (N=16)
January 15, 2011
Desert Renewable Energy Conservation Plan (DRECP) Baseline Biology Report